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Cheshire Wildlife Trust

Heteroptera and Diptera surveys in the Delamere Forest, 2013-2017

by

Phil Brighton

32, Wadeson Way, Croft, Warrington WA3 7JS

@hotmail.co.uk

on behalf of

Cheshire Wildlife Trust

Version 1.0

October 2017

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Abstract This report provides the results of a series of and diptera surveys carried out in the Delamere Forest itself and some of the satellite woodland and bogs. A full list is given of the 460 recorded and their distribution across the surveyed area. This species list is interpreted in terms of habitat assemblages using the PANTHEON software recently made available by the Biological Records Centre. This showed a strong representation of wet woodland species in the sample. The national assemblages of peatland and decaying wood species were much less well represented but included a higher proportion of rare or scarce species. Of particular note was the find in 3 new locations of the Orthonevra intermedia: Delamere remains the only known British location for this species following the original discovery in 2003. The Red Databook cranefly Idioptera linnei was found at Abbots Moss for the first time since 1969, only the second record in the Delamere area since then. Both these species should benefit from the restoration of the Delamere mossland. Introduction In 2003, at an early stage of the Delamere Lost Mosses project Martin Drake was commissioned to carry out an extensive survey of terrestrial invertebrates across the Delamere area1. The bulk of the records from this survey were of beetles (Coleoptera) and true (Diptera), but other orders were also covered. The methods used were sweep-netting, pitfall trapping and direct observation on walks in 27 of the very numerous peat basins in the main block of Delamere forest. An additional 4 peat bodies in the surrounding area (Thieves Moss and Leech Mere in SJ5669, Gull Moss in SJ6068, and Sherratt’s Rough in SJ6169) were also surveyed.

This report presents results from my own voluntary and amateur surveys of heteroptera and diptera in this area over the past five seasons. The earlier stages of this work have been described in two earlier reports2,3. Comparison of the results with those of Ref 1 gave confidence that these surveys could make a significant additional contribution to knowledge of the Forest’s invertebrate fauna. Further surveys have been carried out in the succeeding two years, covering additional areas and also extending the range of families covered. These surveys have not been limited to the peat basins surveyed in Ref 1.

The method of sampling based on sweep-netting of vegetation supplemented by direct visual observations (and capture if required for identification) remains as described in Ref 2. For the purposes of presenting the results, the area covered has been divided into eight parts. The following table lists these and the main specific sites within these visited during the surveys:

Abbots Moss area Shemmy Moss, South Bog, Whitegate Way East Finney’s Basin, Harthill Moss Hatchmere area Blain’s Moss, Norley Moss, Hatchmere wood North Alvanley Basin, Bainsbridge, Doolittle, Ham Pool Primrosehill Harrow Hill, Tirley Hollow, Urchin’s Kitchen South Blakemere, Hunger Hill, Linmer South-west Black Lake, Great, Midgel, Hockenhull, Little Midgel West Harrison’s, New Pale, Whitemoor Valleys

Table 1 towards the end of this report lists the dates of visits and areas visited as well as the number of records obtained. As in the earlier reports, a “record” denotes the presence of a species in a specific 100m square (ie six-figure grid reference) on a specific date. Owing to the size and complexity of the forest, many of the surveys were also explorations with samples being taken along a lengthy itinerary. Where areas of particularly distinctive and productive habitat have been found repeat visits have been made. The maximum number of records in one day was 164, but the number was much lower on other occasions if other activities were being carried out on the day, if it

Page 2 of 30 was early or late in the season with fewer species to be found, or if bad weather curtailed proceedings.

Further summarising this information according to the months in which records were obtained gives the following overview:

Area Mar Apr May Jun Jul Aug Sep Total Abbots Moss area 17 11 63 91 East 61 61 Hatchmere area 31 58 123 118 168 498 North 19 99 12 35 96 17 278 Primrosehill 23 23 South 33 3 96 23 155 South-west 58 155 120 333 West 8 1 129 159 297 Total number of records 23 58 265 294 175 652 269 1736

This table* shows that particular attention has been paid to the CWT reserve comprising Norley Moss and the Hatchmere wood, both because of the easy access but also the different character of the wet woodland there from the rest of the Delamere Forest. “Hatchmere” was also frequently visited by earlier dipterists (see Ref 2) giving the possibility of finding longer-term changes in the fauna, though this aspect is not explored in the current report. The bias to recording in August has not been intentional: indeed May and June are generally regarded as the peak months for diptera diversity.

It should be noted that some of the records in this report are yet to be verified by the local recording centres or national recording schemes.

Species recorded Tables 2-7 list the species recorded for each of the areas defined above. The grouping of the data largely follows those explained in the two previous reports2,3, except that the calyptrate fly families are now listed separately: this is because the scope of species covered has been increased thanks to the acquisition of recent identification keys for most of these families.

The right-hand column in Tables 2-7 indicates species not recorded in the 2003 survey by Martin Drake. Species recorded in 2003 but not in the 2013-17 surveys are not listed. The following table compares the coverage of the two sets of data in terms of species groups.

Group Drake (2003) Current Surveys Not recorded by Combined Drake (2003) total Terrestrial heteroptera 9 60 53 62 Craneflies 75 74 28 103 38 47 17 55 120 85 23 143 Calyptrates 33 109 90 123 Other diptera 161 85 30 191 Total no. of species 437 460 242 677

* The total number of records is 3 greater than in Table 1 because 3 ad-hoc records from digital photographers were added (1 of Phalacrocera replicata and 2 of Tanyptera atrata).

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As noted above, the current surveys have produced 1736 records of species by 6-figure grid location and day. The 2003 data are reported in terms of the detection or not of each species at the 31 individual peat basins over the survey period from 2-18 July. On this basis the total number of diptera and heteroptera records was 2,206. Many of the smaller basins fit well within a 100m square. The largest, Linmer North is approximately 300m across, but Ref 1 notes that the core swamp occupied a small part. Thus there is a rough equivalence can be claimed in the numbers of records in the two surveys.

There are however numerous differences. The present survey has not been restricted to the close proximity of the peat basins, but has aimed to cover as large a range of habitats as possible including bracken areas, wayside vegetation and wet woodlands in order to explore the overall biodiversity of the site. This may account for the larger numbers of species of heteroptera and calyptrates found in the present surveys. The 2003 report indicates that all the specimens gathered during a fixed period of sweeping at each location were retained and identified, while in the current surveys specimens were selected from the net in order to limit overload during identification. As a result the 2003 survey achieved considerably longer species lists for groups with many smaller species such as the Empidoidea and the Ephydridae (shore-flies). A further difference between the surveys is that the present series were not restricted to a few weeks of the season, so covering species with early and late flight periods.

Thus the two surveys can be considered roughly equivalent in coverage though they represent differently biased samples from the invertebrate fauna of the Delamere area. It seems unlikely that the habitat management carried out since 2003 will have greatly changed the range of species present, though of course it should encourage an increase in abundance of the bog specialist species.

PANTHEON analysis The species list from the current surveys has been run through the PANTHEON software which became available on the BRC website during 2017. This software is based on a database linking species to their larval and adult food “guilds”, to their characteristic habitats, and to other associated species such as the hosts of parasitic flies. It also flags up species with a conservation designation and for certain special habitats gives a score representing how specific the species is to that habitat. It should be noted however that it currently contains data for only 3047 fly species whereas the total number on the British list is over 7000.

Table 8 lists those species from the present surveys which are flagged up in PANTHEON as having a national conservation designation and/or a score reflecting their fidelity to certain special habitats. The PANTHEON data for other species can be viewed on the BRC website. Various statistics can be generated and they combine to give an overall picture of the Delamere environment, as follows. First, Figure 1 overleaf shows the breakdown of the species list by feeding guild. In both cases predators are the largest category. Larvae feeding on decaying matter are the next largest category, while for adults the non-feeding and nectar-feeding species contribute very similar proportions. The first of these two groups is all the craneflies, while nectar-feeding species include (), Syrphidae (hoverflies) and other smaller fly families. That the latter are so well represented is surprising given that flowers with nectar are largely confined to sides of tracks and paths in the Forest. However bramble and heather will also provide feeding opportunities in their

Page 4 of 30 season. Areas of bramble were largely avoided during both sets of surveys, because of the difficulty of sweep netting.

Figure 1: proportion of species by feeding guild as larvae (left) and adults (right)

The Table below contains results from PANTHEON showing the number of species associated with each habitat represented in the data. As some species have multiple associations, some habitats appearing on the Table are clearly irrelevant. The figure for representation is the number of species recorded as a proportion of the total number in the PANTHEON database for that habitat. The guidance states that 10-20% may indicate good quality while 21% or more certainly suggests a good proportion of characteristic species. These figures are reached for shaded woodland floor and wet woodland in our sample, but not for peatland.

% No. of No. of Broad biotope Habitat represent- designated SQI species ation species tree-associated shaded woodland 161 14 7 117 floor open habitats tall sward & scrub 86 3 100 wetland peatland 81 7 10 150 wetland running water 60 6 7 137 wetland wet woodland 55 20 5 130 tree-associated wet woodland 54 21 5 130 wetland marshland 43 5 100 tree-associated decaying wood 22 2 3 145 tree-associated arboreal 20 2 100 open habitats short sward & bare 10 <1 100 ground open habitats upland 3 2 100 coastal saltmarsh 1 <1 100 coastal brackish pools & 1 <1 100 ditches

Each species is assigned a species quality score (SQS) according to their conservation status. Non- designated species score 1 while the SQS increases from 4 to 32 as one progresses from the

Page 5 of 30 nationally scarce or notable to the rarest categories such as critically endangered. The SQI is 100 times the sum of the scores divided by the number of species, so that 100 indicates a lack of any designated species. On this measure the peatland habitat scores highest because of the high number of associated species with a designation. Decaying wood also shows up better on this measure: although the 22 species found are only 2% of the national total there are three species with a designation.

Table 8 also shows a “habitat score” for species associated with certain specific assemblage types (SATs – see PANTHEON website for further explanation). Here A denotes species confined to a specific habitat while b, c etc denote progressively weaker association – see further below in the discussion of species of particular note from the survey.

Species of note This section provides comments on the species contributing to the characteristic habitats identified by the PANTHEON analysis above, as listed in Table 8. Terrestrial Heteroptera The terrestrial bugs in the sub-order Heteroptera are mainly associated with warm dry environments, and so it is not surprising that few register as characteristic in this survey. The most frequently encountered in the surveys were the predatory common flower bug Anthocoris nemorum and the green capsid bug Lygocoris pabulinus which can both be found virtually anywhere. Bryocoris pteridis and Monalocoris filicis are small mirid bugs feeding on bracken and other ferns.

The only bug species appearing in Table 8 is Cymus glandicolor though that is because of a loose association with calcareous grassland, which is not relevant here. Lamproplax picea is worth mentioning as it is a sphagnum specialist with few other Cheshire records. Gastrodes abietum is known as the spruce cone bug and this appears to be the first find in Cheshire, though it is more frequent in southern England. Craneflies Craneflies (families Cylindrotomidae, Limoniidae, , Ptychopteridae and Tipulidae) are the best represented group in Table 8, reflecting their reputation as good environmental indicators. These species are variously associated with acid mires and various types of seepage. There are also species with some association with coarse woody debris (CWD), a term used specifically to refer to larger bores of wood deposited in streams or water bodies.

Particularly pleasing is the find at Abbots Moss of Idioptera linnei with its nationally rare status (and SQS of 16). This attractive species with its banded wings was the subject of extensive surveys by Pete Boardman across Shropshire and Cheshire in the mid-2000s, when it turned up at Wybunbury Moss and Little Budworth Common. The only previous Delamere records in the last 50 years are from Hatchmere in 1990 and Abbots Moss in 1969. The 2017 find (pictured left) was from the edge of a pool on the edge of the South Bog, where two males were found by sweep-netting (one was released). This species has always been elusive and confined to a few areas of North Wales and Northern England, where it is found in sphagnum pools.

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Another scarce acid mire species Erioptera nielseni was found in the Hockenhull basin: the scatter of previous records has been from the area around Abbots Moss. The woodland seepage species Dicranomyia lucida is new to Delamere, found by a stream near the western edge of the Forest, and recorded in Cheshire only once before.

Valuable additions to the data are the two records of the attractive wasp- mimic Tanyptera atrata from digital photographs sent in by other observers. The male with its comb-like antennae is seen on the fingertip of a rubber glove in the photograph on the right. The larvae develop in decaying wood, but the adults seem to be elusive, apparently appearing briefly around early June.

Hoverflies Ref 3 reported the find of a female of the small nearly all-black hoverfly Orthonevra intermedia on the wet heath at the west end of Blakemere on 20 August 2015. Delamere remains the only location for this species in Britain, found during Martin Drake’s 2003 survey and formally reported in Ref 4. The last two seasons have yielded further records in new areas of the Forest: one male at Harrison’s on 6th July 2016 and two males and two females at Black Lake on 7th June 2017, a surprisingly early date. This spread of records across most of the Forest apart from the Eastern sector 14 years after the initial discovery certainly suggest that the species is well established and benefitting from the restoration of its bog habitat.

Martin Drake1 remarked on the small range of hoverflies found, which as discussed above may be associated with a relative lack of nectaring plants, on which many of the adults depend. However, Table 8 shows that several species have larvae dependent on the characteristic Delamere habitats. A particularly unusual find associated with coarse woody debris is Xylota florum with only a few previous Cheshire records, and apparently in decline nationally. Empidoidea This superfamily includes the , known as the long-legged flies (though not nearly as long-legged as the craneflies), and the “dance-flies”, formerly all in the . The English name of the latter derives from the dancing and swarming behaviour of many species. They are mainly predatory on other , often with a long and menacing proboscis. This family has now been split, with a fair proportion of the British genera now being placed in and the two much smaller families Brachystomatidae (represented by three species in Table 5) and .

Like the craneflies, the Dolichopodidae are recognised as particularly useful as indicators of habitat quality. They can occur in large numbers but being small with many similar species, the scarcer ones are prone to be overlooked. Undoubtedly the 2003 survey was more thorough for this group, as Martin Drake is the national expert for this family.

Perhaps the most noteworthy find in this group from the present surveys is the hybotid fly borealis. I found two females at Hockenhull on 18 May 2017. Martin Drake recorded it from three different locations, Alvanley, Limner North and Harthill so it is widespread in the Forest. Like Orthonevra intermedia it seems to be a relict from wide-spread boggy conditions following the end of the Ice Age. The NBN Atlas has only 4 records nationally, from Staffordshire and Yorkshire.

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Calyptrates The calyptrates constitute a grouping of the most highly evolved diptera, mostly typically fly-like and bristly such as houseflies (Muscidae) and blowflies (Calliphoridae). The present surveys have been able to add a relatively large number of species thanks to the recent availability of new or revised keys to all except a few very small families. It is not clear why more from this group were not recorded in the 2003 survey, but it may be because habitat associations are less well-known and so they are of less relevance for habitat evaluation.

For many of the species there is no information available in PANTHEON, and only the following three register on Table 8 as contributors to increased habitat scores.

 The nominally rare Lispocephala brachialis is a smallish grey and orange muscid, which I found at Blains and Blakemere Mosses. There are indications that it is not now as rare as previously thought. Indeed this year I found the species in my own Warrington garden, possibly linked to presence of the liverwort Marchantia which PANTHEON lists as an association.  The family includes the dungflies of the Scathophaga but also many species with plant-eating (phytophagous larvae). The scarce nationally rufimana has clear associations with Carex species on acid mires, and also occurs on the Manchester Mosses.  Norellia spinipes is normally found near the larval food-plant which is daffodils. In the present survey it was swept from the access track to Norley Moss which runs past a garden. This species was first found in Britain in the 1960s but has since been found over an increasingly wide area, including my own garden in Warrington and two other such locations in Cheshire.

The is the family of parasitic flies with 266 British species and so similar in size to the Syrphidae (hoverflies). Most species are encountered as isolated individuals and the present surveys with only 9 species include the only two recorded in Ref 1. Possibly the paucity of tachinids reflects a low abundance of the lepidopterous hosts of most species.

Of those which were found, collaris is known to attack the heather leaf beetle Lochmaea suturalis and Myxexoristops stolidus is a parasite of sawflies. Cinochira atra and the large and distinctive Phasia depend on heteropteran hosts. The latter with its purple-tinged wings was photographed (right) on wayside hogweed near Barnsbridge.

No species from the family were recorded in the 2003 survey. This may be because comprehensive identification keys had yet to be produced for what was regarded as a difficult family of mainly greyish and blackish flies. However with 245 species many of which have strong plant associations either as phytophagous larvae or as nectaring adults, this family is probably as significant contributor to the diptera fauna as the hoverflies. I have myself been recording the family only for the past two seasons so many more species are probably yet to be found than the 27 listed in Table 6. The genus Chirosia is prominent with 5 species, a high proportion of the British total of 12. Their larvae feed on ferns, including bracken for certain species, so they are part of a distinct element of the Delamere ecology. Other diptera The remaining species recorded, as listed in Table 7, come from a wide variety of families and are only linked by being covered by being relatively easy to identify. In the 2003 survey this group

Page 8 of 30 included the greatest number of species, with several families beyond the scope of the present surveys. Of the nationally scarce species noted in Table 8, Sapromyza albiceps () was found at 9 locations in 2003. I started recorded this family only in the middle of this year, and recorded this smallish yellow species only at Black Lake.

The nationally scarce Themira germanica is an addition to the list for Delamere and for Cheshire. It rather resembles a small black ant. It is a member of the small family Sepsidae, which generally breed in dung*. There are five common species of the genus Sepsis and these are some of the most commonly encountered flies on the Delamere peat basins, several species often being found together.

Amongst all these other diptera, the soldierflies and allies are the most commonly recorded and many are believed to be good indicators of habitat quality. In that respect, the results are fairly disappointing, the highlight being the soldier fly Beris fuscipes found in several locations in both the 2003 and present surveys. This is species was not flagged up by PANTHEON, but according to other sources it is nationally notable or scarce.

Discussion The above represents an initial exploration of the use of the PANTHEON database to analyse diptera data in the Lancashire and Cheshire region. The software has only become available this year, and there appear to be no published examples of its application to the heteroptera and diptera fauna of specific sites. The significance of the results above is therefore uncertain at present. It is intended in the near future to carry out similar analysis for the Manchester Mosses where a similar level of surveying have been carried out over the last 5 years5, and comparison of the results may shed more light on whether the surveys and analysis are producing a realistic assessment of the sites.

While PANTHEON is based on measures of national rarity, it is also of interest to consider the Delamere area in the regional context of Lancashire and Cheshire. Ref 1 identified many species as “local”, but stated that this term is “not rigidly defined, but loosely means species confined to a particular habitat type (usually associated with better quality examples of that habitat), a particular geographic area, or species that are too widespread to warrant Nationally Scarce (Notable) status but are nevertheless infrequently encountered”: no reference to any national or regional listing of local species was given, however. Such information is available in the 1959 account of the Diptera of Lancashire and Cheshire by Kidd and Brindle6, though there too the precise basis of the term “local” is unclear. Furthermore, that publication covered only about half of the species in the order – the projected Part 2 never appeared – and the information remains in printed form only. However, a start has been made on updating the regional checklist by compiling the data accumulated in local record centres, the NBN and other sources. So far this has been carried out for the soldierflies and allies7 and for the Sepsidae family8: these lists include the numbers of records for species.

Nevertheless the PANTHEON assessment of the species list has given some interesting indications of the value of the Delamere area for the heteroptera and diptera fauna. Although the peat basins have yielded the largest quality score, wet woodland species are the best represented group. Decaying wood species were rather few, but those that were present had the second largest quality score. In terms of adult feeding resources, it was surprising that nectar-feeding species were the second largest category, as flower-rich areas are scarce in the Forest: if habitat management can

* The association of this species with Anatidae (ducks, geese and swans) in PANTHEON presumably refers to the dung of these birds.

Page 9 of 30 increase such areas, this could be beneficial for the other habitats where the larvae of these species occur.

The PANTHEON scores are however heavily dependent on the number of scarce or rare species. Even when these have been recorded they are often represented by only one or two specimens. This seems to be the inherent in the extremely small samples in terms of time and space that even the present surveys represent. It is hoped that a method of taking account of the full range of species present and comparing the numbers of records at the site with those across the whole region can be developed.

Acknowledgements Thanks are due to Katie Piercey of Cheshire Wildlife Trust for allowing access to the reserves, to Martin Drake for supplying a copy of his report, and to the observers who have contributed additional photographic records.

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Table 1: dates of survey visits, areas visited and number of records obtained (ie species present in a 100m square).

07/05/2013 16/06/2013 19/08/2013 16/05/2014 04/08/2014 01/09/2014 09/04/2015 11/08/2015 20/08/2015 29/09/2015 14/03/2016 20/05/2016 15/06/2016 06/07/2016 24/08/2016 21/09/2016 18/05/2017 07/06/2017 25/07/2017 04/08/2017 Total Grand

Abbots Moss area 17 63 11 91 East 37 24 61 Hatchmere area 53 57 65 31 90 123 78 497 North 10 47 15 18 1 80 52 35 17 2 277 Primrosehill 23 23 South 3 40 23 35 32 21 156 South-west 1 23 58 154 97 333 West 1 8 159 129 297 Grand Total 17 15 53 104 120 60 57 160 138 114 23 84 123 164 63 95 58 156 11 118 1733

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Table 2: count of records for individual heteroptera species by area

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Recording group/species Total Abbots Moss area Moss Abbots East ar Hatchmere North Primrosehill South South West by Drake Not found (2003) PLANT BUGS & ALLIES  Anthocoris confusus 1 1 2  Anthocoris nemoralis 1 1 Anthocoris nemorum 2 2 12 9 2 5 6 7 45  Apolygus spinolae 1 1 1 3  Atractotomus magnicornis 1 1  Blepharidopterus angulatus 1 1 2 4  Bryocoris pteridis 1 4 1 3 1 10  Closterotomus norwegicus 1 1  Cyllecoris histrionius 1 1 2  Cymus glandicolor 1 1 2 4  Cymus melanocephalus 1 3 1 3 2 1 11  Cyrtorhinus caricis 1 2 1 4  Deraeocoris lutescens 1 1  Dicyphus globulifer 1 1  Dicyphus pallicornis 1 1  Dicyphus stachydis 1 1 2  Gastrodes abietum 1 1  Heterotoma planicornis 1 1  Kleidocerys ericae 1 1  Kleidocerys resedae 1 4 1 1 1 1 9  Lamproplax picea 1 1 Leptopterna ferrugata 1 1  Liocoris tripustulatus 1 2 1 4  Lygocoris pabulinus 2 2 5 2 2 5 18  Lygocoris rugicollis 1 1  Lygus rugulipennis 1 1  Malacocoris chlorizans 1 1  Mecomma ambulans 2 2  Monalocoris filicis 5 3 1 3 4 16  Nabis ericetorum 1 2 3 Nabis limbatus 3 3 2 1 2 11  Nabis rugosus 1 1  contaminatus 1 3 4 1 9  Notostira elongata 1 1  Orius vicinus 2 2  Orthops campestris 1 1 Orthotylus ericetorum 6 6 

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Recording group/species Total Abbots Moss area Moss Abbots East ar Hatchmere North Primrosehill South South West by Drake Not found (2003)  Orthotylus marginalis 1 1  Phylus melanocephalus 1 1 2  Pithanus maerkelii 1 1  Plagiognathus arbustorum 1 3 1 1 6  Psallus montanus 3 3  Psallus perrisi 1 1  Scolopostethus affinis 1 1  Scolopostethus decoratus 1 1 1 3  Scolopostethus thomsoni 1 1 1 1 4 Stenodema calcarata 1 6 1 1 1 1 11 Stenodema holsata 1 8 1 1 11 Stenodema laevigata 1 1 2 1 5  Stenotus binotatus 1 1  Trapezonotus desertus 1 1  Trigonotylus ruficornis 1 1 SHIELDBUGS & ALLIES  Acanthosoma haemorrhoidale 1 1  Dolycoris baccarum 1 1  Elasmostethus interstinctus 2 3 1 6  Elasmucha grisea 2 2  Palomena prasina 1 1 1 1 4  Picromerus bidens 2 2  Troilus luridus 1 1 WATER BUGS Saldula saltatoria 1 3 1 5 Total number of records 17 12 86 38 2 24 39 40 258 Number of species 15 9 34 18 1 15 22 24 60 53

Table 3: count of records for individual cranefly species by area

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Species area Moss Abbots East area Hatchmere North Primrosehill South South West Total Grand by Not found Drake(2003) Achyrolimonia decemmaculata 1 2 1 4 Austrolimnophila ochracea 4 3 1 5 2 15 Cheilotrichia cinerascens 1 2 1 4

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Species area Moss Abbots East area Hatchmere North Primrosehill South South West Total Grand by Not found Drake(2003)  Cylindrotoma distinctissima 1 2 3 Dicranomyia chorea 2 1 3 Dicranomyia distendens 1 1 Dicranomyia fusca 2 4 6  Dicranomyia lucida 1 1 Dicranomyia modesta 8 1 1 10 Dicranomyia morio 1 1 2 Dicranophragma nemorale 1 1 2 Dicranota bimaculata 1 1 2 Dolichopeza albipes 1 2 2 5  Epiphragma ocellare 2 2 Erioconopa trivialis 1 1 1 1 4 Erioptera fuscipennis 1 1 4 1 7 Erioptera lutea 2 1 1 4  Erioptera nielseni 1 1 Euphylidorea aperta 2 2 Euphylidorea meigenii 1 2 1 2 6 Helius flavus 1 1 Helius longirostris 1 1 2  Idioptera linnei 1 1  Ilisia occoecata 1 1  Limonia flavipes 1 1 Limonia macrostigma 5 5 Limonia nubeculosa 1 1 8 5 1 4 1 21  Limonia phragmitidis 1 1 2  Metalimnobia quadrinotata 1 1 Molophilus appendiculatus 2 1 3 Molophilus bifidus 1 1  Molophilus bihamatus 1 1  1 1 2 3 1 3 9 Molophilus medius 2 2 Molophilus occultus 1 1 Molophilus ochraceus 1 1  Molophilus serpentiger 3 3 Neolimonia dumetorum 1 1 2 4  Ormosia depilata 1 1  Paradelphomyia dalei 1 1 2 Paradelphomyia senilis 3 2 5

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Species area Moss Abbots East area Hatchmere North Primrosehill South South West Total Grand by Not found Drake(2003)  rivosa 1 1 Phalacrocera replicata 1 1 2 Phylidorea ferruginea 1 4 1 1 7 Phylidorea fulvonervosa 4 1 1 6 Phylidorea squalens 1 3 2 2 8 Pilaria discicollis 3 3 Prionocera turcica 1 2 2 6 4 1 16 Pseudolimnophila lucorum 1 1 Pseudolimnophila sepium 2 2 Ptychoptera lacustris 2 1 3 Ptychoptera minuta 1 2 1 4 Rhipidia maculata 2 1 3  Rhypholophus varius 1 3 1 5 Symplecta stictica 1 1 2  Tanyptera atrata 1 1 2  Tipula alpium 1 1 2 4  Tipula confusa 1 1 2 Tipula fulvipennis 2 1 3 Tipula lateralis 1 1  Tipula luna 1 1  Tipula luteipennis 5 5  Tipula melanoceros 3 3  Tipula oleracea 1 1 1 3 Tipula paludosa 1 1 2  Tipula pruinosa 1 1  Tipula rufina 1 1 Tipula variicornis 1 1 2 Tipula yerburyi 1 1  Trichocera regelationis 1 1  Tricyphona immaculata 3 2 3 1 9  Ula mollissima 2 1 3 Ula sylvatica 1 1 1 3 Totals 10 16 112 42 1 20 37 25 263 Number of species 8 13 54 25 1 14 21 19 74 28

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Table 4: count of records for individual hoverfly species by area

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Species area Moss Abbots East Hatchm North Primrosehill South South West Total by Not found Drake(2003) Baccha elongata 1 1 1 3 Chalcosyrphus nemorum 3 1 4  albitarsis 1 1 1 1 4  Cheilosia bergenstammi 2 2 Cheilosia illustrata 1 3 4  Cheilosia pagana 1 1  Cheilosia scutellata 1 1 solstitialis 2 5 7 Chrysogaster virescens 2 1 1 4  Dasysyrphus tricinctus 1 1 Episyrphus balteatus 1 4 2 2 3 12 Eristalis arbustorum 1 1 2  Eristalis nemorum 1 1 Eristalis pertinax 4 5 3 4 1 4 21 Eristalis tenax 2 1 2 1 6 Eupeodes corollae 1 1  Eupeodes latifasciatus 1 1  Eupeodes luniger 1 1 2 Helophilus hybridus 2 2 1 2 2 1 1 1 8  metallina 1 1 glaucia 1 3 4  Leucozona laternaria 1 1  hirtella 2 2 Melanostoma mellinum 1 4 1 6 Melanostoma scalare 2 1 3 1 3 2 1 13 Myathropa florea 1 1 Neoascia tenur 2 1 1 4 Orthonevra intermedia 1 1 1 3 Platycheirus albimanus 2 1 1 2 5 1 12 Platycheirus clypeatus 1 3 2 1 2 9  Platycheirus fulviventris 1 1 Platycheirus granditarsus 1 1 2 Platycheirus occultus 1 2 1 1 5 Platycheirus scutatus agg. 1 1 2 Sericomyia lappona 2 2 Sericomyia silentis 1 1 1 4 1 8 Sphaerophoria philanthus 2 2 

Page 16 of 30

ere area ere

west

-

Species area Moss Abbots East Hatchm North Primrosehill South South West Total by Not found Drake(2003) Sphegina clunipes 2 1 1 2 6 Syritta pipiens 1 2 1 2 6 Syrphus ribesii 1 1 2 2 6  Syrphus vitripennis 1 1 2  Tropidia scita 1 1 Volucella pellucens 1 1 2  Xylota florum 1 1 Xylota segnis 2 3 1 6 Xylota sylvarum 1 1  Grand Total 14 1 46 27 0 35 29 44 196 Number of species 9 1 26 18 0 20 19 27 47 17

Table 5: count of records for individual Empidoidea species by area

west

-

Family/Species Abbots Moss area Moss Abbots East area Hatchmere North Primrosehill South South West Total Grand by Drake Not found (2003) BRACHYSTOMATIDAE  Gloma fuscipennis 2 2 Heleodromia immaculata 1 1  Trichopeza longicornis 3 1 2 5 11 DOLICHOPODIDAE  Achalcus cinereus 1 1 Anepsiomyia flaviventris 3 3 6 argentina/perplexa 1 2 1 4 curvipes 1 12 3 2 1 5 24 Campsicnemus loripes 1 7 2 1 2 13 Campsicnemus scambus 2 18 4 1 3 3 31 Chrysotus femoratus/neglectus 1 1 2 Chrysotus gramineus 3 2 5 discifer 1 1 3 2 3 2 12 Dolichopus griseipennis 2 2 Dolichopus latilimbatus 1 1 Dolichopus lepidus 2 2 4  Dolichopus picipes 1 1 Dolichopus plumipes 1 3 4

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west

-

Family/Species Abbots Moss area Moss Abbots East area Hatchmere North Primrosehill South South West Total Grand by Drake Not found (2003) Dolichopus popularis 1 1 Dolichopus simplex 1 1 Dolichopus ungulatus 1 1 2 4 Hercostomus aerosus 8 10 3 10 10 41 Hercostomus brevicornis 1 6 7 Hercostomus cupreus 5 7 3 8 1 24 Hercostomus metallicus 7 2 2 4 15  impigra 1 1  Medetera truncorum 1 1 Poecilobothrus nobilitatus 1 1 2 Rhaphium appendiculatum 1 1  Rhaphium caliginosum 1 1  Rhaphium crassipes 1 1 Rhaphium monotrichum 1 1 Sciapus platypterus 2 2 4 Sybistroma obscurellum 1 1 1 3 6 Sympycnus desoutteri 2 1 3 3 9 Syntormon denticulatum 1 1 Syntormon pallipes 4 1 1 1 7 Xanthochlorus galbanus 1 1 EMPIDIDAE Chelifera precatoria 1 1 2 Chelipoda albiseta 1 1 2 guttata 1 1 1 2 5 Dolichocephala oblongoguttata 1 1 aestiva 1 1  Empis chioptera 1 1  Empis nigripes 1 1 Empis praevia 2 3 2 7 14  Empis tessellata 1 1 2 chorica 1 1 2 Hilara cornicula 1 1  Hilara fulvibarba 1 1 Hilara intermedia 1 1 Hilara interstincta 1 1 2 Hilara litorea 2 2  Hilara lurida 1 1 Hilara manicata 1 1 3 5 Hilara maura 1 1 1 3 

Page 18 of 30

west

-

Family/Species Abbots Moss area Moss Abbots East area Hatchmere North Primrosehill South South West Total Grand by Drake Not found (2003) Hilara nigrina 4 4  Hilara nigrohirta 1 1 Hilara obscura/flavipes 1 1 Hilara rejecta 2 2 Phyllodromia melanocephala 2 3 5  Rhamphomyia anomalipennis 1 1  Rhamphomyia erythrophthalma 2 1 1 4 Rhamphomyia flava 1 1  Rhamphomyia longipes 1 1 Rhamphomyia nigripennis 1 1 2  Rhamphomyia tibiella 4 4  Rhamphomyia umbripennis 1 1 2 4 8 HYBOTIDAE intermedia 1 1 4 3 9 1 1 2 2 5 7  inermis 1 1 culiciformis 3 1 6 6 2 4 8 30 1 2 2 5 10 Leptopeza borealis 1 1 glabricula 3 8 3 2 4 20  stigmatella 2 2 ciliaris 2 2 4 Platypalpus longicornis 1 1 1 2 5 Platypalpus longiseta 1 1 Platypalpus minutus 1 1 Platypalpus pallidiventris 2 1 3 6 Platypalpus pectoralis 1 1 nubila 1 1  Trichina elongata 1 1  Trichinomyia flavipes 2 2 Grand Total 15 8 115 81 0 26 91 102 438 Number of species 10 7 37 40 0 15 37 39 85 23

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Table 6: count of records for individual calyptrate fly species by area

west

-

Family/Species Abbots Moss area Moss Abbots East area Hatchmere North Primrosehill South South West Total Grand by Not found (2003) Drake ANTHOMYIIDAE  Alliopsis silvestris 3 3  cannabina 1 1  Anthomyia liturata 1 1  1 1  Botanophila discreta 1 1  Botanophila fugax 1 1 2 4  Botanophila striolata 1 1  Chirosia albitarsis 2 1 3  Chirosia crassiseta 1 1 2  Chirosia flavipennis 2 2 4  Chirosia grossicauda 3 1 2 6  Chirosia histricina 5 5  Delia florilega 1 1 2 4  Delia platura 1 1 3 1 6  Egle ciliata 1 1  Eustalomyia histrio 1 1  urbica 1 1  Hylemya vagans 4 1 1 6  Hylemya variata 1 1  Hylemyza partita 1 1  Lasiomma latipenne 1 1  Lasiomma seminitidum 3 3  Paradelia intersecta 5 5  geniculata 1 1 2  aestiva 1 1 2  Pegoplata infirma 1 1  Zaphne caudata 1 1 CALLIPHORIDAE  Bellardia vulgaris 1 1  Calliphora vomitoria 1 1 2  Lucilia ampullacea 1 1 Lucilia caesar 1 1 2  Melanomya nana 2 2 4 Pollenia pediculata 2 1 3  fuscula 1 1  Fannia lustrator 1 1 Fannia mollissima 1 1 2 

Page 20 of 30

west

-

Family/Species Abbots Moss area Moss Abbots East area Hatchmere North Primrosehill South South West Total Grand by Not found (2003) Drake  Fannia pallitibia 2 2  Fannia parva 1 1 2 Fannia polychaeta 1 3 4  Fannia postica 1 1  Fannia rondanii 1 1 Fannia serena 1 1 4 1 7  Fannia similis 1 1 Fannia subsimilis 1 1  Fannia umbrosa 1 1 MUSCIDAE  cilipes 2 1 1 4  Azelia nebulosa 1 1  Azelia triquetra 1 1  Brontaea humilis 1 1  femoralis 1 1  Coenosia rufipalpis 2 2 4  Coenosia testacea 1 1  Coenosia tigrina 1 1 2 4 Eudasyphora cyanella 1 1 2  Graphomya maculata 1 1  nigra 1 2 1 4  Hebecnema nigricolor 1 2 1 4  Hebecnema umbratica 2 2  Hebecnema vespertina 1 1  depuncta 2 2 1 2 7  Helina evecta 1 1 2  Helina impuncta 2 1 3  Helina reversio 1 1 2  albipuncta 1 1 2  Hydrotaea cyrtoneurina 1 1  Hydrotaea irritans 1 1 2 1 1 6  Hydrotaea militaris 1 4 1 6  Lispocephala brachialis 1 1 2  Lispocephala erythrocera 1 4 2 1 8  Mesembrina meridiana 1 1 simplex 1 1 2  Muscina levida 1 1 2  ancilla 1 1 2  Mydaea electa 1 1 Mydaea urbana 1 1 

Page 21 of 30

west

-

Family/Species Abbots Moss area Moss Abbots East area Hatchmere North Primrosehill South South West Total Grand by Not found (2003) Drake  Myospila meditabunda 1 1  angelicae 1 3 1 5  Phaonia errans 1 1  Phaonia fuscata 1 1  Phaonia pallida 1 1  Phaonia palpata 1 2 1 4  Phaonia rufiventris 2 2 4  Phaonia subventa 1 1 2  Phaonia tuguriorum 2 1 3  Pseudocoenosia abnormis 1 1  Pseudocoenosia solitaria 1 2 3 Schoenomyza litorella 1 1  SARCOPHAGIDAE Sarcophaga carnaria 1 1 Sarcophaga variegata 1 1 SCATHOPHAGIDAE Cleigastra apicalis 1 1 2 1 1 1 3 Cordilura ciliata 1 2 3 Cordilura pudica 1 1 Cordilura rufimana 2 1 3  Norellia spinipes 1 1 Norellisoma spinimanum 1 1  Pogonata barbata 1 1 Scathophaga furcata 2 1 3 6  Scathophaga inquinata 1 2 1 4 Scathophaga stercoraria 1 1 3 9 4 8 3 29 TACHINIDAE  Cinochira atra 1 1 Dexiosoma caninum 1 1  Medina collaris 1 1  Myxexoristops stolidus 1 1  Pales pavida 1 1 2  Phasia hemiptera 1 1 Siphona geniculata 1 1 2  Tachina ursina 1 1  Voria ruralis 1 1 Totals 9 9 61 46 12 23 91 27 278 Number of species 8 8 42 32 5 17 56 22 109 90

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Table 7: count of records for individual fly species not covered above, by area

west

-

Recording group or family/species Abbots Moss area Moss Abbots East area Hatchmere North Primrosehill South South West Total Grand by Not found (2003) Drake Sylvicola cinctus 2 1 1 1 1 6 Sylvicola punctatus 2 1 1 1 5  Asteia amoena 1 1  Bibio lanigerus 1 1 2  Dilophus febrilis 1 1 1 3 CAMPICHOETIDAE  Campichoeta obscuripennis 1 1 CLUSIIDAE  Clusiodes albimana 1 1 ETC.  Conops quadrifasciatus 1 1 Lonchoptera bifurcata 1 1 2 2 6 Lonchoptera lutea 2 4 9 7 1 1 1 4 29  Palloptera scutellata 1 3 1 5  Palloptera trimacula 1 1 Palloptera umbellatarum 1 1 Seioptera vibrans 1 1  Sicus ferrugineus 2 1 3 DIASTATIDAE Diastata adusta 2 1 3 Diastata fuscula 1 1 DROSOPHILIDAE Scaptomyza flava 1 1 Neuroctena anilis 1 2 2 1 1 7 EPHYDRIDAE Ilythea spilota 1 1  Limnellia quadrata 1 1 Notiphila maculata 1 1 Parydra coarctata 1 1 2 Parydra littoralis 3 3 FUNGUS GNATS  Platyura marginata 1 1 Sciara hemerobioides 1 1 

Page 23 of 30

west

-

Recording group or family/species Abbots Moss area Moss Abbots East area Hatchmere North Primrosehill South South West Total Grand by Not found (2003) Drake Suillia affinis 1 1 Suillia atricornis 1 1 Suillia bicolor 1 1 Suillia fuscicornis 1 1  Suillia humilis 1 1  Suillia notata 1 1  Suillia ustulata 1 1 Suillia variegata 1 3 4 LAUXANIIDAE rorida 1 1 2  fasciata 1 1  litura 1 2 3 Sapromyza albiceps 1 1 Sapromyza sexpunctata 1 1 Tricholauxania praeusta 1 1 OPETIIDAE Opetia nigra 4 2 6 Geomyza tripunctata 1 1 1 1 4 florum 2 9 5 3 3 3 25 Opomyza germinationis 2 1 3 2 1 2 5 16 Opomyza petrei 2 2  Hydromya dorsalis 1 1 Pherbina coryleti 1 1 Renocera pallida 2 1 3 Tetanocera elata 2 2 Tetanocera ferruginea 2 2 SEPSIDAE Nemopoda nitidula 1 1 2 4 Sepsis cynipsea 2 1 6 2 1 4 5 21 Sepsis flavimana 1 1 Sepsis fulgens 1 4 2 1 3 2 6 19 Sepsis orthocnemis 2 4 1 2 2 3 14 Sepsis punctum 2 1 3 6 Sepsis violacea 1 1 2 1 1 6  Themira germanica 1 1  Themira minor 1 1 SOLDIERFLIES AND ALLIES

Page 24 of 30

west

-

Recording group or family/species Abbots Moss area Moss Abbots East area Hatchmere North Primrosehill South South West Total Grand by Not found (2003) Drake  Beris chalybata 1 2 1 4 Beris fuscipes 1 1 1 3 Chorisops tibialis 1 1 cristatus 1 1  Dioctria baumhaueri 1 1 Haematopota pluvialis 1 1 1 3  Microchrysa polita 1 1 Rhagio lineola 1 2 1 2 4 10 Rhagio scolopaceus 1 1 Sargus iridatus 1 1 2  Copromyza equina 2 1 3 Copromyza nigrina 1 1 2  Crumomyia fimetaria 1 1 Leptocera fontinalis 1 2 1 1 5 Lotophila atra 2 2 Opacifrons coxata 1 1 Opacifrons humida 1 1 1 3 Rachispoda lutosa 1 1 STILT & STALK FLY Calobata petronella 1 1 2  Chamaepsila humeralis 1 1 Loxocera albiseta 1 1 1 1 4 TEPHRITIDAE  Chaetostomella cylindrica 1 1  Tephritis formosa 1 1  Tephritis neesii 1 2 3  Terellia tussilaginis 1 1 Xyphosia miliaria 1 1 2 Grand Total 26 15 78 44 8 27 46 59 303 Number of species 21 11 37 21 7 20 33 32 85 30

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Table 8: species with a conservation status and/or habitat specificity score according to PANTHEON

Species Family Conservation Habitat Habitat score Associations status

Sylvicola cinctus Anisopodidae shaded woodland floor coarse woody debris: c Phalacrocera replicata Cylindrotomidae Notable peatland acid mire: C, grazing marsh - salinity: 0, grazing marsh - status: 3 Achalcus cinereus Dolichopodidae NS peatland Arthropoda Dolichopus lepidus Dolichopodidae NS peatland acid mire: C Arthropoda Hercostomus aerosus Dolichopodidae peatland acid mire: C Arthropoda Hercostomus brevicornis Dolichopodidae NS peatland; shaded woodland floor; Arthropoda wet woodland Medetera impigra Dolichopodidae NS decaying wood Fagales Xanthochlorus galbanus Dolichopodidae NS Chelifera precatoria Empididae running water coarse woody debris: e, ERS Arthropoda (Diptera): 3

Euthyneura inermis Hybotidae (LR);NS decaying wood Fagus Leptopeza borealis Hybotidae NR;NT Sapromyza albiceps Lauxaniidae Notable shaded woodland floor Achyrolimonia Limoniidae decaying wood coarse woody debris: c Fagales decemmaculata Austrolimnophila Limoniidae decaying wood; shaded woodland coarse woody debris: c Acer, Quercus ochracea floor

Dicranomyia chorea Limoniidae running water; shaded woodland coarse woody debris: c floor; tall sward & scrub Dicranomyia distendens Limoniidae Notable peatland; running water acid mire: B, seepage (acid- Sphagnum neutral): A

Dicranomyia fusca Limoniidae running water; shaded woodland coarse woody debris: c, Fagales floor; wet woodland seepage (woodland): B

Page 26 of 30

Species Family Conservation Habitat Habitat score Associations status Dicranomyia lucida Limoniidae Notable running water; shaded woodland seepage (woodland): A Fagales floor; wet woodland Epiphragma ocellare Limoniidae decaying wood coarse woody debris: c Fagales Erioptera nielseni Limoniidae Notable peatland; running water acid mire: A, seepage (acid- neutral): A

Euphylidorea meigenii Limoniidae peatland acid mire: B Helius longirostris Limoniidae marshland coarse woody debris: e Idioptera linnei Limoniidae RDB 1 peatland acid mire: A Limonia flavipes Limoniidae shaded woodland floor coarse woody debris: c Limonia macrostigma Limoniidae running water; shaded woodland coarse woody debris: c Fagales floor; wet woodland

Limonia nubeculosa Limoniidae decaying wood; shaded woodland coarse woody debris: c Fungi floor

Limonia phragmitidis Limoniidae shaded woodland floor coarse woody debris: c Fungi Molophilus Limoniidae running water; shaded woodland coarse woody debris: e Fagales appendiculatus floor; wet woodland Molophilus bifidus Limoniidae running water; shaded woodland seepage (woodland): B Fagales floor; wet woodland Molophilus bihamatus Limoniidae Notable running water; shaded woodland Fagales floor; wet woodland Molophilus medius Limoniidae running water; shaded woodland coarse woody debris: e Fagales floor; wet woodland Molophilus occultus Limoniidae peatland; shaded woodland floor; acid mire: C, seepage (acid- Fagales wet woodland neutral): C Neolimonia dumetorum Limoniidae decaying wood coarse woody debris: d Alnus, Betula, Quercus Paradelphomyia dalei Limoniidae running water; shaded woodland seepage (woodland): C Fagales floor; wet woodland

Page 27 of 30

Species Family Conservation Habitat Habitat score Associations status

Paradelphomyia senilis Limoniidae running water; shaded woodland seepage (woodland): A Fagales floor; wet woodland Phylidorea ferruginea Limoniidae marshland; peatland coarse woody debris: d Phylidorea squalens Limoniidae peatland acid mire: B Rhipidia maculata Limoniidae decaying wood; shaded woodland coarse woody debris: d Acer, Betula, floor Quercus

Rhypholophus varius Limoniidae shaded woodland floor coarse woody debris: c Symplecta stictica Limoniidae brackish pools & ditches, peatland, coarse woody debris: c saltmarsh

Cymus glandicolor Lygaeidae marshland calcareous grassland: Low Carex Lispocephala brachialis Muscidae RDB 3 running water; shaded woodland Arthropoda, floor; wet woodland Marchantiophyta Dicranota bimaculata Pediciidae running water coarse woody debris: e Tricyphona immaculata Pediciidae marshland; peatland acid mire: C, coarse woody debris: d/e

Ptychoptera lacustris Ptychopteridae running water; shaded woodland seepage (woodland): C Fagales floor; wet woodland Chrysopilus cristatus peatland; shaded woodland floor; coarse woody debris: c Fagales wet woodland Cordilura rufimana Scathophagidae Notable peatland acid mire: C Carex Norellia spinipes Scathophagidae Notable shaded woodland floor Narcissus Themira germanica Sepsidae Notable peatland Anatidae Chrysogaster solstitialis Syrphidae peatland; running water; shaded seepage (woodland): A Fagales, Quercus woodland floor; wet woodland

Chrysogaster virescens Syrphidae peatland; running water; shaded acid mire: C, seepage (acid- Fagales woodland floor; wet woodland neutral): B, seepage (woodland): B

Page 28 of 30

Species Family Conservation Habitat Habitat score Associations status

Lejogaster metallina Syrphidae peatland; running water; shaded seepage (acid-neutral): B Fagales woodland floor; wet woodland

Melanogaster hirtella Syrphidae marshland; peatland seepage (calcareous): B Typha Orthonevra intermedia Syrphidae DD;NS Sericomyia lappona Syrphidae seepage (acid-neutral): C Sericomyia silentis Syrphidae peatland seepage (acid-neutral): C

Sphegina clunipes Syrphidae decaying wood coarse woody debris: a/b Fagales

Xylota florum Syrphidae decaying wood coarse woody debris: a/b Fagales

Xylota segnis Syrphidae decaying wood coarse woody debris: c Fagales Dolichopeza albipes Tipulidae running water seepage (acid-neutral): C, seepage (woodland): C Prionocera turcica Tipulidae marshland; peatland acid mire: C Tanyptera atrata Tipulidae Notable decaying wood Alnus, Betula Tipula fulvipennis Tipulidae running water; shaded woodland seepage (woodland): C Fagales floor; wet woodland

Tipula lateralis Tipulidae running water seepage (calcareous): B, seepage (soft rock cliff): B, seepage (woodland): B Tipula luteipennis Tipulidae marshland; peatland; running water seepage (woodland): C

Tipula melanoceros Tipulidae peatland acid mire: A Juncus Tipula oleracea Tipulidae peatland coarse woody debris: d Tipula yerburyi Tipulidae Notable running water acid mire: C, seepage (woodland): C

Page 29 of 30

REFERENCES

1. C. M. Drake, The Lost Meres & Mosses of Delamere: Terrestrial Invertebrate Appraisal of Stage Two Basins, Delamere Forest, Cheshire, Report for Colin Hayes, Ecology-First, Dec 2003. 2. P. Brighton, Bug and Fly Recording in the Delamere Forest, report for Cheshire Wildlife Trust, Version 1.0, Dec 2014. 3. P. Brighton, Bug and Fly Recording in the Delamere Forest – 2015 Update, report for Cheshire Wildlife Trust, Version 1.0, Jan 2016. 4. C. M. Drake, “Orthonevra intermedia Lundbeck, 1916 (Diptera, Syrphidae) new to Britain”, Dipterists Digest (Second Series), 13(2006)87-91. 5. P. Brighton, Bug and Fly recording on the Manchester Mosses – 2015 update, report for Cheshire and Lancashire Wildlife Trusts, Version 1.0, Jan 2016. 6. L. N. Kidd & A. Brindle, The Diptera of Lancashire and Cheshire, Part 1, Lancashire and Cheshire Fauna Committee, 1959. 7. P. Brighton, The Diptera of Lancashire and Cheshire: Soldierflies and Allies, unpublished report, Draft 1.0, Jan 2017. 8. P. Brighton, The Diptera of Lancashire and Cheshire: Sepsidae (Acalypratae: ), unpublished report, Draft 1.0, Feb 2017.

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